JPH0691281A - Treatment of organic waste water containing phosphorus - Google Patents

Treatment of organic waste water containing phosphorus

Info

Publication number
JPH0691281A
JPH0691281A JP24186392A JP24186392A JPH0691281A JP H0691281 A JPH0691281 A JP H0691281A JP 24186392 A JP24186392 A JP 24186392A JP 24186392 A JP24186392 A JP 24186392A JP H0691281 A JPH0691281 A JP H0691281A
Authority
JP
Japan
Prior art keywords
phosphorus
carbonic acid
treatment
water
tower
Prior art date
Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
Pending
Application number
JP24186392A
Other languages
Japanese (ja)
Inventor
Yutaka Tsukuda
豊 佃
Yoshiaki Harada
吉明 原田
Kenichi Yamazaki
健一 山崎
Noboru Yamada
登 山田
Tadashi Takadoi
忠 高土居
Yoshihiro Eto
良弘 恵藤
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
Kurita Water Industries Ltd
Osaka Gas Co Ltd
Original Assignee
Kurita Water Industries Ltd
Osaka Gas Co Ltd
Priority date (The priority date is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the date listed.)
Filing date
Publication date
Application filed by Kurita Water Industries Ltd, Osaka Gas Co Ltd filed Critical Kurita Water Industries Ltd
Priority to JP24186392A priority Critical patent/JPH0691281A/en
Publication of JPH0691281A publication Critical patent/JPH0691281A/en
Pending legal-status Critical Current

Links

Abstract

PURPOSE:To treat a waste water efficiently at a low treatment cost by treating a water treated by wet type oxidation to remove carbonic acid and adding a calcium compound to the resulting waste water, regarding a treatment method which involves calcium compound addition after wet type oxidization treatment of organic waste water containing phosphorus and removal of phosphorus by making the phosphorus insoluble. CONSTITUTION:Raw water containing the substances to be oxidized and phosphorus is supplied to a wet type oxidation reaction tower 1, the substances are oxidized and decomposed, the resulting gas-liquid mixed solution is separated in a gas-liquid separating tower 2, and the gas is released to air and the separated liquid is sent to a carbonic acid removing tower 3. Carbonic acid is efficiently removed in the carbonic acid removing tower 3 and a calcium compound such as slaked lime, etc., is added to the resulting carbonic acid-removed water in a reaction tank 4 where phosphorus is made insoluble, and a part of SS is also returned from a solid-liquid separation tank 5 in a post stage. The slaked lime and carbonic acid-removed water are mixed and stirred in the reaction tank 4 and phosphorus is converted into hydroxyl apatite and thus becomes insoluble. Separation treatment is then carried out in a solid-liquid separation tank 5 and the supernatant water is discharged outside and a part of separated sludge is returned to the reaction tank 4 and the rest is discharged outside.

Description

【発明の詳細な説明】Detailed Description of the Invention

【0001】[0001]

【産業上の利用分野】本発明はリンを含む有機性廃水の
処理方法に係り、特に、し尿等のリンを含む高濃度有機
廃水を湿式酸化処理した後カルシウム化合物を添加し、
リンを不溶化して除去する方法において、カルシウム化
合物の使用量の低減及び汚泥発生量の低減を図るリンを
含む有機性廃水の処理方法に関する。
BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to a method for treating an organic wastewater containing phosphorus, and more particularly, to a high-concentration organic wastewater containing phosphorus such as human waste which is subjected to a wet oxidation treatment and then a calcium compound is added thereto
In a method for insolubilizing and removing phosphorus, the present invention relates to a method for treating organic wastewater containing phosphorus for reducing the amount of calcium compound used and the amount of sludge generated.

【0002】[0002]

【従来の技術】従来、被酸化物を比較的高濃度に含む廃
水、例えばし尿、下水又はし尿を生物学的に処理した際
に発生する余剰汚泥或いは消化汚泥、石炭のガス化・液
化廃水、都市ゴミの熱分解により生成する廃水、製糸工
場、繊維染色工場、食品工場、化学工場、石油精製工場
その他の各種工場から排出される工場廃水等の処理方法
として湿式酸化処理が行なわれている。
2. Description of the Related Art Conventionally, wastewater containing a relatively high concentration of oxides such as human waste, sewage or excess sludge generated when biologically treating human waste, digested sludge, coal gasification / liquefaction wastewater, BACKGROUND ART Wet oxidation treatment is performed as a treatment method of wastewater generated by thermal decomposition of municipal waste, factory wastewater discharged from yarn mills, fiber dyeing factories, food factories, chemical factories, petroleum refining factories and other various factories.

【0003】この湿式酸化処理は、高圧タンクからなる
湿式酸化反応塔内に上述の廃水を導入し、酸素の存在
下、高温、高圧に維持して被酸化物を炭酸ガス、硝酸、
窒素ガス、水分に分解するもので、この際酸化分解反応
を効率よく行なわせるために、湿式酸化反応塔内には酸
化触媒の充填槽が内蔵されている。
In this wet oxidation treatment, the above-mentioned wastewater is introduced into a wet oxidation reaction tower consisting of a high-pressure tank and maintained at high temperature and high pressure in the presence of oxygen so that the oxides to be oxidized are carbon dioxide gas, nitric acid,
It decomposes into nitrogen gas and water, and in this case, in order to efficiently carry out the oxidative decomposition reaction, a filling tank of an oxidation catalyst is built in the wet oxidation reaction tower.

【0004】この酸化触媒とてしてはチタニア(酸化チ
タニア)、ジルコニア(酸化ジルコニア)、アルミナ、
シリカ、シリカ−アルミナ、活性炭、或いはニッケル、
ニッケル−クロム、ニッケル−クロム−アルミニウム、
ニッケル−クロム−鉄等の金属多孔体からなる単体に
鉄、マンガン、コバルト、ニッケル、ルテニウム、ロジ
ウム、パラジウム、イリジウム、白金、銅、金及びタン
グステン並びにこれらの酸化物、更には二塩化ルテニウ
ム、二塩化白金等の塩化物、硫化ルテニウム、硫化ロジ
ウム等の硫化物の水に対し不溶性又は難溶性の化合物を
担持させたものが用いられている。
As the oxidation catalyst, titania (titania oxide), zirconia (zirconia oxide), alumina,
Silica, silica-alumina, activated carbon, or nickel,
Nickel-chromium, nickel-chromium-aluminum,
Iron-manganese-cobalt-nickel-ruthenium-rhodium-palladium-iridium-platinum-copper-gold and tungsten and their oxides, and ruthenium dichloride and dichloride A substance in which a compound such as a chloride such as platinum chloride or a sulfide such as ruthenium sulfide or rhodium sulfide and which is insoluble or hardly soluble in water is supported is used.

【0005】しかして、このような湿式酸化反応塔から
の湿式酸化処理水から更にリンを除去する方法として、
リン不溶化剤を添加して反応液を固液分離することが行
なわれている(例えば特開平2−31889、同2−3
1896)。
However, as a method for further removing phosphorus from the wet oxidation treated water from such a wet oxidation reaction tower,
A reaction solution is solid-liquid separated by adding a phosphorus insolubilizer (for example, JP-A-2-31889 and 2-3).
1896).

【0006】[0006]

【発明が解決しようとする課題】しかしながら、上記従
来の処理方法にあっては、湿式酸化反応塔の処理水にリ
ン不溶化剤を添加しリン除去を行なうように構成されて
いるため、リン不溶化剤の使用量が多く、薬剤費がかさ
むという欠点があった。
However, in the above conventional treatment method, the phosphorus insolubilizing agent is added to the treated water of the wet oxidation reaction tower to remove the phosphorus, so that the phosphorus insolubilizing agent is removed. However, there is a drawback that the drug cost is high because of the large amount used.

【0007】即ち、湿式酸化反応塔からの処理水中に
は、その分解生成物である炭酸が多く含まれているた
め、この処理水に直接リン不溶化剤として、例えば水酸
化カルシウム(Ca(OH)2 )を添加すると、このC
a(OH)2 は炭酸との反応に消費されてしまう。
That is, since the treated water from the wet oxidation reaction tower contains a large amount of carbonic acid, which is a decomposition product of the treated water, the treated water is directly treated with a phosphorus insolubilizing agent such as calcium hydroxide (Ca (OH)). 2 ) is added, this C
a (OH) 2 is consumed in the reaction with carbonic acid.

【0008】しかも、Ca(OH)2 と炭酸との反応で
生じた炭酸カルシウムの汚泥が生成し、その処分費用が
かさむという欠点もあった。
Moreover, there is also a drawback that calcium carbonate sludge produced by the reaction between Ca (OH) 2 and carbonic acid is produced, and the disposal cost thereof is high.

【0009】本発明は上記従来の問題点を解決し、し尿
等のリンを含む高濃度有機廃水を湿式酸化処理した後カ
ルシウム化合物を添加し、リンを不溶化して除去する方
法において、カルシウム化合物の使用量の低減及び汚泥
発生量の低減を可能とするリンを含む有機性廃水の処理
方法を提供することを目的とする。
The present invention solves the above-mentioned conventional problems, and in a method of wet-oxidizing a high-concentration organic wastewater containing phosphorus such as human waste and then adding a calcium compound to insolubilize and remove phosphorus, It is an object of the present invention to provide a method for treating organic wastewater containing phosphorus, which can reduce the amount used and the amount of sludge generation.

【0010】[0010]

【課題を解決するための手段】本発明のリンを含む有機
性廃水の処理方法は、リンを含む有機性廃水を湿式酸化
処理し、その処理水にカルシウム化合物を添加し、リン
を不溶化して除去する方法において、前記湿式酸化処理
水を脱炭酸処理した後、カルシウム化合物を添加するこ
とを特徴とする。
The method for treating organic wastewater containing phosphorus according to the present invention comprises subjecting organic wastewater containing phosphorus to wet oxidation treatment, adding a calcium compound to the treated water, and insolubilizing phosphorus. In the removing method, the wet oxidation treated water is decarbonated, and then a calcium compound is added.

【0011】[0011]

【作用】本発明のリンを含む有機性廃水の処理方法で
は、カルシウム化合物の添加に先立ち、湿式酸化処理水
を脱炭酸するため、湿式酸化処理水中の炭酸がこの脱炭
酸処理で除去される。
In the method for treating organic wastewater containing phosphorus of the present invention, the wet oxidation treated water is decarbonated prior to the addition of the calcium compound, so that the carbonation in the wet oxidation treated water is removed by this decarboxylation treatment.

【0012】このため、湿式酸化処理水中の炭酸との反
応でカルシウム化合物が消費されることがなくなり、カ
ルシウム化合物使用量の低減が図れる。また、湿式酸化
処理水中の炭酸とカルシウム化合物との反応で炭酸カル
シウムの汚泥が生成することなく、発生汚泥量が低減さ
れる。
Therefore, the calcium compound is not consumed by the reaction with carbonic acid in the wet oxidation treated water, and the amount of the calcium compound used can be reduced. In addition, the amount of generated sludge is reduced without generating sludge of calcium carbonate due to the reaction between the carbonic acid in the wet oxidation treated water and the calcium compound.

【0013】このため薬剤コスト、汚泥処分コストの低
減が図れ、処理効率、処理コストは大幅に改善される。
Therefore, the chemical cost and the sludge disposal cost can be reduced, and the treatment efficiency and the treatment cost can be greatly improved.

【0014】[0014]

【実施例】以下に図面を参照して本発明の実施例につい
て詳細に説明する。
Embodiments of the present invention will be described below in detail with reference to the drawings.

【0015】図1は本発明のリンを含む有機性廃水の処
理方法の一実施例を示す系統図である。
FIG. 1 is a system diagram showing an embodiment of the method for treating organic wastewater containing phosphorus according to the present invention.

【0016】図中、1は周知の酸化触媒1Aが充填され
ている高圧タンクからなる湿式酸化反応塔である。この
湿式酸化反応塔1は、図示しない加熱手段により250
〜290℃に加温されるとともに、加圧手段により70
〜90kg/cm2 に加圧され、更にガス供給手段によ
り酸素が供給されている。
In the figure, reference numeral 1 is a wet oxidation reaction column comprising a high-pressure tank filled with a known oxidation catalyst 1A. The wet oxidation reaction tower 1 is heated to 250 by a heating means (not shown).
It is heated to ~ 290 ° C and is heated to 70
The pressure is increased to 90 kg / cm 2 , and oxygen is further supplied by the gas supply means.

【0017】なお、加温は装置始動時に外部の熱源で行
なわれるが、装置が定常運転状態になると原水中の酸化
燃焼により行なうことができる。
Although the heating is performed by an external heat source at the time of starting the apparatus, it can be performed by oxidative combustion in raw water when the apparatus is in a steady operation state.

【0018】また、湿式酸化反応塔1には酸化触媒を必
ずしも充填する必要がないが、本実施例のように酸化触
媒1Aを充填することにより、効率良く酸化処理するこ
とができる。
Although the wet oxidation reaction tower 1 does not necessarily need to be filled with an oxidation catalyst, it can be efficiently oxidized by filling it with the oxidation catalyst 1A as in this embodiment.

【0019】湿式酸化反応塔1には、原水供給配管11
より被酸化物及びリンを含む原水が供給され、原水中の
被酸化物は湿式酸化反応塔1内で酸化されて、炭酸ガ
ス、窒素ガス、水に分解され、その気液混合液は配管1
2を経て気液分離塔2へ送給される。この配管12には
図示しない熱交換器が設けられており、これにより原水
供給配管11の原水が熱交換されて加温され熱回収が行
なわれている。
The wet oxidation reaction tower 1 has a raw water supply pipe 11
Raw water containing oxidant and phosphorus is supplied from the oxidant, the oxidant in the raw water is oxidized in the wet oxidation reaction tower 1 and decomposed into carbon dioxide gas, nitrogen gas, and water, and the gas-liquid mixed liquid is pipe 1
It is fed to the gas-liquid separation tower 2 via 2. The pipe 12 is provided with a heat exchanger (not shown), by which the raw water in the raw water supply pipe 11 is heat-exchanged and heated to recover heat.

【0020】気液分離塔2で分離されたガス成分は、図
示しない減圧弁を備える配管13を経てサイクロンセパ
レータへ送給され、サイクロンセパレータで分離された
ガスは大気へ放出される。一方、気液分離塔2の分離液
は、配管14より、後述の脱炭酸塔3へ送給される。サ
イクロンセパレータの分離液分もこの分離液と共に脱炭
酸塔3へ送給される。
The gas component separated in the gas-liquid separation column 2 is sent to the cyclone separator through a pipe 13 equipped with a pressure reducing valve (not shown), and the gas separated by the cyclone separator is released to the atmosphere. On the other hand, the separated liquid of the gas-liquid separation tower 2 is fed to the decarbonation tower 3 described later through the pipe 14. The separated liquid component of the cyclone separator is also sent to the decarbonation tower 3 together with this separated liquid.

【0021】脱炭酸塔3の型式には特に制限はなく、ラ
ッシヒリング3A等が充填され、配管15より、塔下部
から空気やN2 ガスを吹き込む方式でも水底下部から曝
気する方式でも良く、また、操作圧力は常圧、減圧のい
ずれでも良い。
The type of the decarbonation tower 3 is not particularly limited, and may be filled with Raschig rings 3A and the like, and a method of blowing air or N 2 gas from the lower part of the tower through the pipe 15 or aeration from the lower part of the water bottom. The operating pressure may be either normal pressure or reduced pressure.

【0022】この脱炭酸塔3において、湿式酸化処理水
中の炭酸は効率的に除去され、炭酸が除去された脱炭酸
処理水は、配管16よりリン不溶化反応槽4へ供給され
る。
In the decarbonation tower 3, carbon dioxide in the wet oxidation treated water is efficiently removed, and the decarbonated water from which the carbonic acid is removed is supplied to the phosphorus insolubilization reaction tank 4 through the pipe 16.

【0023】リン不溶化反応槽4には、配管17より消
石灰(Ca(OH)2 )等のカルシウム化合物が不溶化
剤として添加されると共に、後工程の固液分離槽5から
のSSの一部が配管18より返送されている。ここで、
Ca(OH)2 添加量はpH計4Aによって制御され、
通常の場合、pH9.5〜10.5程度となるようにC
a(OH)2 の添加が行なわれる。4Bは攪拌機であ
る。
In the phosphorus insolubilization reaction tank 4, a calcium compound such as slaked lime (Ca (OH) 2 ) is added as an insolubilizing agent from a pipe 17, and a part of SS from the solid-liquid separation tank 5 in the subsequent step is added. Returned from the pipe 18. here,
The amount of Ca (OH) 2 added is controlled by the pH meter 4A,
Normally, C is adjusted so that the pH is about 9.5 to 10.5.
Addition of a (OH) 2 is performed. 4B is a stirrer.

【0024】なお、リン不溶化剤のカルシウム化合物と
しては、Ca(OH)2 の他、生石灰、塩化カルシウム
などを用いても良い。
As the calcium compound of the phosphorus insolubilizing agent, quick lime, calcium chloride, etc. may be used in addition to Ca (OH) 2 .

【0025】リン不溶化反応槽4内でCa(OH)2
脱炭酸処理水とが混合攪拌されると、脱炭酸処理水中の
リンはヒドロキシルアパタイト(Ca5 OH(PO4
3 )となり不溶化する。不溶化されたリンを含む処理水
は配管19より固液分離槽5に送給され分離処理される
が、ここで、処理水の清澄化のために、高分子凝集剤を
この配管19に直接又は別途反応槽を設けて添加すると
良い。
When Ca (OH) 2 and decarbonated water are mixed and stirred in the phosphorus insolubilization reaction tank 4, phosphorus in the decarbonated water is converted into hydroxylapatite (Ca 5 OH (PO 4 )).
3 ) and becomes insoluble. The treated water containing insolubilized phosphorus is fed to the solid-liquid separation tank 5 through the pipe 19 for separation treatment. Here, in order to clarify the treated water, the polymer coagulant is directly or directly supplied to the pipe 19. It is advisable to install a separate reaction tank and add the solution.

【0026】この固液分離槽5の上澄水は配管20より
処理水として系外へ排出され、一方、分離汚泥の一部は
前述の如く、配管18よりリン不溶化反応槽4に返送さ
れ、残部は配管21より系外へ排出される。
The supernatant water of the solid-liquid separation tank 5 is discharged to the outside of the system through the pipe 20 as treated water, while a part of the separated sludge is returned to the phosphorus insolubilization reaction tank 4 through the pipe 18 and the rest is left. Is discharged from the system through the pipe 21.

【0027】なお、固液分離槽5としては沈殿槽、砂濾
過槽、膜濾過装置などを適用することができる。
As the solid-liquid separation tank 5, a precipitation tank, a sand filtration tank, a membrane filtration device or the like can be applied.

【0028】以下に具体的な実施例及び比較例を挙げ
て、本発明をより詳細に説明する。
The present invention will be described in more detail below with reference to specific examples and comparative examples.

【0029】実施例1 図1に示す本発明方法により、下記処理条件にて、し尿
を850リットル/hrの流量で処理し、リン不溶化反
応槽に添加したCa(OH)2 添加量と、処理水のリン
濃度及び汚泥発生量を表1に示した。
Example 1 By the method of the present invention shown in FIG. 1, human waste was treated under the following treatment conditions at a flow rate of 850 liters / hr, and the amount of Ca (OH) 2 added to the phosphorus insolubilization reaction tank and the treatment were performed. Table 1 shows the phosphorus concentration of water and the amount of sludge generated.

【0030】処理条件 湿式酸化反応塔: 温度=270℃ 圧力=90kg/cm2 滞留時間=90分 脱炭酸塔: 滞留時間=16分 空気量(G/L)=10 リン不溶化反応槽: pH=10.0 汚泥返送量=原水量に対して50% 比較例1 脱炭酸塔を設けなかったこと以外は実施例1と同様に処
理し、リン不溶化反応槽に添加したCa(OH)2 添加
量と、処理水のリン濃度及び汚泥発生量を表1に示し
た。
Treatment condition Wet oxidation reaction tower: Temperature = 270 ° C. Pressure = 90 kg / cm 2 Residence time = 90 minutes Decarbonation tower: Residence time = 16 minutes Air amount (G / L) = 10 Phosphorus insolubilization reaction tank: pH = 10.0 Amount of sludge returned = 50% with respect to the amount of raw water Comparative Example 1 The amount of Ca (OH) 2 added to the phosphorus insolubilization reaction tank which was treated in the same manner as in Example 1 except that no decarbonation tower was provided. Table 1 shows the phosphorus concentration and the amount of sludge generated in the treated water.

【0031】[0031]

【表1】 [Table 1]

【0032】表1より明らかなように、本発明の方法に
従って、リン不溶化処理に先立って脱炭酸処理を行なう
ことにより、カルシウム化合物の必要添加量及び汚泥発
生量を大幅に低減することができる。
As is clear from Table 1, by performing the decarboxylation treatment prior to the phosphorus insolubilization treatment according to the method of the present invention, the required addition amount of the calcium compound and the sludge generation amount can be greatly reduced.

【0033】[0033]

【発明の効果】以上詳述した通り、本発明のリンを含む
有機性廃水の処理方法によれば、リンを含む有機性廃水
を湿式酸化処理し、その処理水にカルシウム化合物を添
加し、リンを不溶化して除去する方法において、カルシ
ウム化合物使用量を低減すると共に、汚泥発生量を大幅
に低減して、薬剤コスト、汚泥処理コストの低廉化が達
成される。従って、リンを含む有機性廃水を低処理コス
トにて効率的に処理することが可能とされる。
As described above in detail, according to the method for treating organic wastewater containing phosphorus of the present invention, the organic wastewater containing phosphorus is subjected to wet oxidation treatment, the calcium compound is added to the treated water, and phosphorus is added. In the method of insolubilizing and removing slag, the amount of calcium compound used is reduced and the amount of sludge generated is significantly reduced, and the chemical cost and sludge treatment cost are reduced. Therefore, it becomes possible to efficiently treat the organic wastewater containing phosphorus at a low treatment cost.

【図面の簡単な説明】[Brief description of drawings]

【図1】図1は本発明のリンを含む有機性廃水の処理方
法の一実施例を示す系統図である。
FIG. 1 is a system diagram showing an embodiment of a method for treating organic wastewater containing phosphorus according to the present invention.

【符号の説明】[Explanation of symbols]

1 湿式酸化反応塔 2 気液分離塔 3 脱炭酸塔 4 リン不溶化反応槽 5 固液分離槽 1 Wet oxidation reaction tower 2 Gas-liquid separation tower 3 Decarbonation tower 4 Phosphorus insolubilization reaction tank 5 Solid-liquid separation tank

───────────────────────────────────────────────────── フロントページの続き (72)発明者 山崎 健一 大阪府大阪市中央区平野町四丁目1番2号 大阪瓦斯株式会社内 (72)発明者 山田 登 東京都新宿区西新宿3丁目4番7号 栗田 工業株式会社内 (72)発明者 高土居 忠 東京都新宿区西新宿3丁目4番7号 栗田 工業株式会社内 (72)発明者 恵藤 良弘 東京都新宿区西新宿3丁目4番7号 栗田 工業株式会社内 ─────────────────────────────────────────────────── ─── Continuation of front page (72) Kenichi Yamazaki 4-1-2, Hirano-cho, Chuo-ku, Osaka City, Osaka Prefecture Osaka Gas Co., Ltd. (72) Noboru Yamada 3--4, Nishi-Shinjuku, Shinjuku-ku, Tokyo No. 7 In Kurita Industry Co., Ltd. (72) Inventor Tadashi Takadoi 3-4 Nishi-Shinjuku, Shinjuku-ku, Tokyo No. 7 In Kurita Industry Co., Ltd. (72) Yoshihiro Eto 3-4 Nishi-Shinjuku, Shinjuku-ku, Tokyo No. 7 Kurita Industry Co., Ltd.

Claims (1)

【特許請求の範囲】[Claims] 【請求項1】 リンを含む有機性廃水を湿式酸化処理
し、その処理水にカルシウム化合物を添加し、リンを不
溶化して除去する方法において、 前記湿式酸化処理水を脱炭酸処理した後、カルシウム化
合物を添加することを特徴とするリンを含む有機性廃水
の処理方法。
1. A method of subjecting an organic wastewater containing phosphorus to a wet oxidation treatment, adding a calcium compound to the treated water to insolubilize and remove phosphorus, wherein the wet oxidation treated water is decarboxylated, and then calcium is added. A method for treating organic wastewater containing phosphorus, which comprises adding a compound.
JP24186392A 1992-09-10 1992-09-10 Treatment of organic waste water containing phosphorus Pending JPH0691281A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP24186392A JPH0691281A (en) 1992-09-10 1992-09-10 Treatment of organic waste water containing phosphorus

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP24186392A JPH0691281A (en) 1992-09-10 1992-09-10 Treatment of organic waste water containing phosphorus

Publications (1)

Publication Number Publication Date
JPH0691281A true JPH0691281A (en) 1994-04-05

Family

ID=17080649

Family Applications (1)

Application Number Title Priority Date Filing Date
JP24186392A Pending JPH0691281A (en) 1992-09-10 1992-09-10 Treatment of organic waste water containing phosphorus

Country Status (1)

Country Link
JP (1) JPH0691281A (en)

Cited By (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2001070951A (en) * 1999-09-01 2001-03-21 Kurita Water Ind Ltd Method for treating phosphorus-containing water
JP2004174386A (en) * 2002-11-27 2004-06-24 Kurita Water Ind Ltd Treatment method for phosphoric acid-containing wastewater
JP2007217576A (en) * 2006-02-17 2007-08-30 Denki Kagaku Kogyo Kk Organic phosphorus treating agent and method for processing organic phosphorus-containing water using the same
WO2013175423A1 (en) * 2012-05-23 2013-11-28 Wetox Limited Sludge treatment method

Cited By (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2001070951A (en) * 1999-09-01 2001-03-21 Kurita Water Ind Ltd Method for treating phosphorus-containing water
JP2004174386A (en) * 2002-11-27 2004-06-24 Kurita Water Ind Ltd Treatment method for phosphoric acid-containing wastewater
JP2007217576A (en) * 2006-02-17 2007-08-30 Denki Kagaku Kogyo Kk Organic phosphorus treating agent and method for processing organic phosphorus-containing water using the same
WO2013175423A1 (en) * 2012-05-23 2013-11-28 Wetox Limited Sludge treatment method
US9637403B2 (en) 2012-05-23 2017-05-02 Wetox Limited Sludge treatment method

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